Soil Disturbance and Recovery After Coppicing a Mediterranean Oak Stand: the Effects of Silviculture and Technology

Total Page:16

File Type:pdf, Size:1020Kb

Soil Disturbance and Recovery After Coppicing a Mediterranean Oak Stand: the Effects of Silviculture and Technology sustainability Article Soil Disturbance and Recovery after Coppicing a Mediterranean Oak Stand: The Effects of Silviculture and Technology Rachele Venanzi 1,2,*, Rodolfo Picchio 1 , Raffaele Spinelli 3 and Stefano Grigolato 2 1 Department of Agricultural and Forest Sciences, University of Tuscia, 01100 Viterbo, Italy; [email protected] 2 Department of Land, Environment, Agriculture and Forestry, Università degli Studi di Padova, 35020 Legnaro, Padova, Italy; [email protected] 3 CNR Institute of Bioeconomy, Via Madonna del Piano 10, 50019 Sesto Fiorentino FI, Italy; [email protected] * Correspondence: [email protected]; Tel.: +39-0761357400; Fax: +39-0761357250 Received: 24 April 2020; Accepted: 12 May 2020; Published: 15 May 2020 Abstract: Traditional coppice management system is one of the most debated topics in the Mediterranean area, as it is a forest management system that accounts for over 23 million hectares. Coppicing is considered the oldest form of sustainable forest management. Its past and current widespread popularity is mainly due to its capacity to positively contribute to the rural economy and ecosystem services. This research aimed at assessing the effect of coppicing on soil characteristics, understanding a possible treatment return time, and evaluating the implementation of proper sustainable forest operations (SFOs) in order to have a better understanding of the disturbance caused by silvicultural treatment and forest operations with two different harvesting techniques. The results demonstrated that physical, chemical, and biological soil features were partially disturbed by the coppicing. Both silvicultural treatment and forest operations influenced soil disturbance. The least impactful technique was extraction by winch, while forwarding resulted in heavier alterations of soil characteristics. It took about five years for the soil to recover its original pre-harvest conditions when the disturbance was caused by the silvicultural treatment alone (non-trafficked areas) and about eight to nine years when the disturbance was the cumulated effect of silvicultural treatment and logging activity (trafficked areas). Keywords: forest operation; skidding-winch; forwarding; soil resilience; Mediterranean area 1. Introduction The coppice management system is one of the most debated topics in the Mediterranean area, as it is a forest management system that accounts for over 23 million hectares [1]. Coppicing is considered the oldest form of sustainable forest management and for this reason it is considered as a natural forest management system [2]. Its past and current popularity is mainly due to its capacity to positively contribute to the rural economy and ecosystem services [3]. Even if this management system presents environmental shortcomings, coppicing represents a valid and flexible management system that requires low inputs and guarantees maintenance of many aesthetic, environmental, social, and economic functions [1,4,5]. Recent findings in ecological and forestry research have highlighted that coppice forests contribute to soil protection and biodiversity conservation [6,7], showing good resilience and significant adaptability to climate change [1,8]. In the past, Mediterranean oak coppice stands were an important source of timber, firewood, and charcoal [9], as well as litter and pasture [10]. Today, they are mostly invested in the production of Sustainability 2020, 12, 4074; doi:10.3390/su12104074 www.mdpi.com/journal/sustainability Sustainability 2020, 12, 4074 2 of 20 wood biomass for energy use due to their capacity to yield sustained amount of raw material at short intervals (on average one cutting cycle is every 12–18 years) [2]. These short cutting cycles could negatively affect soil quality and regeneration vigor [11,12]. Special concern is aroused by the risk for soil degradation connected with frequent machine traffic, which may cause compaction, topsoil removal, and general disturbance [13–16]. Nevertheless, not all logging techniques have the same impact potential and the specific characteristics of any given operation depend on site characteristics, silvicultural management, technological level, and product strategy [17,18]. Furthermore, technological innovations in forest logging and mechanization [19,20] could positively contribute to the improvement of work conditions, compared with traditional logging systems [21,22]. Assessing ground disturbance and minimizing possible damage due to silvicultural treatments and forest operations remain the main focus of sustainable forest management (SFM) [23–25]. In order to reach this aim, numerous suggestions have come from recent research, namely: to minimize the area of soil disturbance and compaction by appropriate operation planning [18,26,27]; to make careful execution of logging operations [28,29]; and to use suitable mechanization [12,30–34]. All this is in consideration of the fact that adequately managed forest ecosystems are highly resilient in the long-term [25,35]. Focusing the attention on coppice systems, there is a need to acquire more information about the impacts due to silvicultural treatment, i.e., actual logging and their interactions. These topics are very often the subject of heated arguments and detailed scientific results are needed to better understand the issue and provide best practice suggestions [2]. For these reasons, the concept of sustainability is frequently overlooked and is not considered as a clear instrument to assess the impact of global change and development. SFM is based on continuous improvements of silvicultural practice and logging methods. In particular, better knowledge is needed on the recovery time of managed forest ecosystems after the inevitable disturbance cause by forest operations, however well they are managed. This is one of the key factors for sustainable use and an important issue both for high forests and coppices [1]. Recent studies [4,5,36] on coppicing in the Mediterranean area have highlighted that within a short time after harvesting (0–3 years), soil and regeneration characteristics show clear signs of recovery. These findings demonstrated that physical, chemical, and biological soil features were only marginally affected by the silvicultural treatment applied, but strongly impacted by harvesting operations. Coppicing maintains a cyclical pattern of extreme changes in ground-level light penetration [1,37,38], producing heterogeneous mosaics of forest in various stages of succession that harbor a rich variety of animals and vascular plants [39–43]. Only efficient planning and management of forest operations and accurate knowledge of the environmental dynamics of the forest will offer high social and environmental benefits and provide various ecosystem services in the long term [44]. These aspects can be guaranteed only through SFM in synergy with sustainable forest operations (SFO) [45]. These tools are essential for proper environmental protection and they are mandatory in order to maintain forests and their multiple functions [45]. In particular, forest operations and coppice management are interesting but delicate issues to be analyzed and evaluated in order to achieve real sustainability. Starting from this background to increase scientific knowledge on the effects of coppicing, the present experiment was designed with four specific goals: to investigate the impact of the silvicultural treatment on soil condition; • to find out how both silvicultural treatment and forest operations influence soil characteristics; • to compare the impact of two different harvesting techniques on soil condition; • to assess the recovery capacity of soil after harvesting in order to project a possible treatment • return time; and evaluating the existence of a proper SFO. Sustainability 2020, 12, 4074 3 of 20 To this end, soil conditions in a Turkey oak coppice located in central Italy were monitored every year for five years after harvesting. 2. Materials and Methods 2.1. Study Sites The study stand was Turkey oak (Quercus cerris L.) forest managed as coppice with standards. The stand was located in Central Italy, Lazio Region, Tarquinia municipality (42◦34037.0700 N, 11◦76040.0000 E). The whole forest covered about 100 ha, with homogeneous elevation, slope gradient, and roughness: 100 m a.s.l., 25% slope gradient and ca 5% of the surface presenting obstacles to machine traffic, respectively. The accessibility of the forest was therefore fairly good (12 m/ha of main forest roads) but the road network in the area included few permanent skid trails. The soil was an Abruptic Luvisol (EpiArenic Cutanic) (WRB, 2014) alluvial, with good depth (ranging from 0.6 to 0.9 m) non-hydromorph and with a neutral reaction. Soil texture was defined as Silty-Loam (SL), due to the high silt content (52%), moderate sand content (38%) and low clay content (10%). Soil field capacity (CC) was 24%, determined using the soil water method [46]. 2.2. Silviculture and Harvesting Technique The study coppice was clear-cut at the age of 35 years, releasing 140 standards per hectare. Standards belonged to three age classes: 35-years-old (60%), 45-years-old (30%), and 60-years-old or older (10%). The harvesting operation was completed within approximately 150 days for the about 100 ha studied. Only one harvesting system was applied, the tree length system (TLS) [47]. One control study area was selected of about 20 ha of coppice unharvested and not impacted for more than 20 years. Felling was performed motor-manually by three teams of two operators equipped
Recommended publications
  • View and Print This Publication
    98 lPAClIJFlI([; §OllJTHWlEST ]fORlE§T & RANGlE lEXlPlERTIMlENT §TAl'TION 1.----- Be r k e ley , C a I i for n i a____ _ ____ 1966_ _ Pacific Madrone ..... a general bibliography for a promising species PHIL1P M.McDONALD and WILLIAM E.SUNDAHL ABSTRACT: Lis t s 60 references, 21 The supply of merchantable of which emphasize the desirable wood working characteristics of the species. hardwoods in California is esti­ mated at about 1.6 billion board feet (Int. 1/4 -inch log rule), ac­ cording to the 1963 Forest Survey. A significant portion of this total is Pacific madrone (Arbutus menziesii PurshJ, whose range extends along the Pacific Coast from southern British Columbia to southern california (fig.l). So far, the demand for this raw material has been rather small largely because no profitable market has existed. Recently, several operators - -both large and small- -have begun to manufacture hardwood products in 0 reg 0 nan d California. Their activities have created interest in the available knowledge on the species, particularly on its wood working charactenstics. This note b r in g s together most of the available references on Pacific madrone. Index Subject Reference Dendrology .4, 7, 14, 25, 32, 33, 53 Ecology... .44, 54 Biotic factor s. · 6, 29 Climatic factors · . 3 Exceptional size and longevity. 1, 2, 12 Forest types · . 50 Injuries Disease. 5,38,52,55 Insects . 28 Management 45 Mensuration Site quality 42 Surveys .. 34,40, 58, 59 Volume tables . .... 24 Forest Serv i ce -U . S . Department of Agriculture 0 0 0 0 0 ~ ~ .
    [Show full text]
  • TB877 Dynamics of Coarse Woody Debris in North American Forests: A
    NATIONAL COUNCIL FOR AIR AND STREAM IMPROVEMENT DYNAMICS OF COARSE WOODY DEBRIS IN NORTH AMERICAN FORESTS: A LITERATURE REVIEW TECHNICAL BULLETIN NO. 877 MAY 2004 by Gregory Zimmerman, Ph.D. Lake Superior State University Sault Ste. Marie, Michigan Acknowledgments This review was prepared by Dr. Gregory Zimmerman of Lake Superior State University. Dr. T. Bently Wigley coordinated NCASI involvement. For more information about this research, contact: T. Bently Wigley, Ph.D. Alan Lucier, Ph.D. NCASI Senior Vice President P.O. Box 340362 NCASI Clemson, SC 29634-0362 P.O. Box 13318 864-656-0840 Research Triangle Park, NC 27709-3318 [email protected] (919) 941-6403 [email protected] For information about NCASI publications, contact: Publications Coordinator NCASI P.O. Box 13318 Research Triangle Park, NC 27709-3318 (919) 941-6400 [email protected] National Council for Air and Stream Improvement, Inc. (NCASI). 2004. Dynamics of coarse woody debris in North American forests: A literature review. Technical Bulletin No. 877. Research Triangle Park, N.C.: National Council for Air and Stream Improvement, Inc. © 2004 by the National Council for Air and Stream Improvement, Inc. serving the environmental research needs of the forest products industry since 1943 PRESIDENT’S NOTE In sustainable forestry programs, managers consider many ecosystem components when developing, implementing, and monitoring forest management activities. Even though snags, downed logs, and stumps have little economic value, they perform important ecological functions, and many species of vertebrate and invertebrate fauna are associated with this coarse woody debris (CWD). Because of the ecological importance of CWD, some state forestry agencies have promulgated guidance for minimum amounts to retain in harvested stands.
    [Show full text]
  • Forest Protection Unifies, Silviculture Divides
    Article Forest Protection Unifies, Silviculture Divides: A Sociological Analysis of Local Stakeholders’ Voices after Coppicing in the Marganai Forest (Sardinia, Italy) Giampiero Branca 1,2, Irene Piredda 2, Roberto Scotti 2 , Laura Chessa 3,4, Ilenia Murgia 2,5 , Antonio Ganga 2 , Sergio Francesco Campus 2, Raffaella Lovreglio 2 , Enrico Guastini 2, Massimiliano Schwarz 6 and Filippo Giadrossich 2,4,* 1 Department of Humanities and Social Sciences, University of Sassari, Piazza Conte di Moriana, 07100 Sassari, Italy; [email protected] 2 Nuoro Forestry School, Department of Agriculture, University of Sassari, 08100 Nuoro, Italy; [email protected] (I.P.); [email protected] (R.S.); [email protected] (I.M.); [email protected] (A.G.); [email protected] (S.F.C.); [email protected] (R.L.); [email protected] (E.G.) 3 AREA Science Park, Padriciano 99, 34149 Trieste, Italy; [email protected] 4 Desertification Research Center, University of Sassari, Viale Italia 39, 07100 Sassari, Italy 5 Department of Architecture, Design and Planning, University of Sassari, Piazza Duomo 6, 07041 Alghero, Italy 6 School of Agricultural Forest and Food Sciences, Bern University of Applied Sciences, Länggasse 85, 3052 Zollikofen, Switzerland; [email protected] * Correspondence: [email protected] Received: 28 May 2020; Accepted: 22 June 2020; Published: 25 June 2020 Abstract: Today, a forest is also understood as a real social actor with multiple-scale influences, capable of significantly conditioning the social, economic, and cultural system of a whole territory. The aim of this paper is to reconstruct and interpret the population’s perception of the silvicultural activities related to traditional use of forest resources of the southwestern Sardinian Marganai State Forest.
    [Show full text]
  • Coppicing: Using a Forester's Tool on Range- Lands Linda Howell Hardesty
    Rangelands 9(3), June 1987 129 Coppicing: Using A Forester's Tool on Range- lands Linda Howell Hardesty The phenomenon of coppicing, widelyused by foresters, ments. The coppicing stump uses the root system and can also bean important range managementtool. Coppice is reserves of the original plant, and under the influence of a defined as "all regeneration that is derived from vegetative chemical "contingency plan" reinitiates growth with proper- sprouting of dormant or adventitious buds." Range manag- ties very different from seedling growth. These properties ers talk about sprouting in conjunction with brush control, can affect forage production and quality. generally in a negative sense, as in: "mesquite's sprouting ability makes control almost impossible." While most people know what sprouting is, coppicingis only vaguely familiaras a managementtool. Foresters use coppice methods to insure a rapid, economical return to full stocking after wood is harvested, to maintain a desirable species and genetic composition, and to shorten rotation times. Following this more positive vein, what advantages might coppicinghave for the range manager interested in improving forage production? Coppiceregeneration and uncut caatinga woodlandsin northeast Brazil. The most familiar phenomenon is the speed with which coppice shoots emerge and grow. Most range managers have seen coppice shoots emerge from charred shrubs withindays ofa range fire, or have cut a tree in theyard only to have it begin almost immediately to fight back. The for- estry literature notes that coppice shoots may out-grow seed- lings for as long as 40 years (Daniel et al. 1979). Coppicing Cutting backcoppice growth of Auxemmaoncocalyx. stumps can provide browse in a hurry.
    [Show full text]
  • Coppice in Brief
    COST Action FP1301 EuroCoppice Innovative management and multifunctional utilisation of traditional coppice forests – an answer to future ecological, economic and social challenges in the European forestry sector Coppice in Brief Authors Rob Jarman & Pieter D. Kofman COST is supported by the EU Framework Programme Horizon 2020 COST is supported by the EU Framework Programme Horizon 2020 COST (European Cooperation in Science and Technology) is a pan-European intergovernmental framework. Its mission is to enable break-through scientifi c and technological developments leading to new concepts and products and thereby contribute to strengthening Europe’s research and innovation capacities. www.cost.eu Published by: Albert Ludwig University Freiburg Gero Becker, Chair of Forest Utilization Werthmannstr. 6 79085 Freiburg Germany Printed by: Albert Ludwig University Freiburg Printing Press Year of publication: 2017 Authors: Rob Jarman (UK) & Pieter D. Kofman (DK) Corresponding author: Rob Jarman, [email protected] Reference as: Jarman, R., Kofman, P.D. (2017). Coppice in Brief. COST Action FP1301 Reports. Freiburg, Germany: Albert Ludwig University of Freiburg. Copyright: Reproduction of this document and its content, in part or in whole, is authorised, provided the source is acknowledged, save where otherwise stated. Design & layout: Alicia Unrau Cover acknowledgements: Simple coppice (grey) based on a drawing by João Carvalho; Leaf vectors originals designed by www.freepik.com (modifi ed) Disclaimer: The views expressed in this publication are those of the authors and do not necessarily represent those of the COST Association or the Albert Ludwig University of Freiburg. COPPI C E (NOUN): AN AREA OF [WOOD]LAND (ON FOREST OR AGRICULTURAL LAND) THAT HAS BEEN REGENERATED FROM SHOOTS AND/OR ROOT SUCKERS FORMED AT THE STUMPS OF PREVIOUSLY FELLED TREES OR SHRUBS.
    [Show full text]
  • Does Forest Certification Conserve Biodiversity?
    Oryx Vol 37 No 2 April 2003 Does forest certification conserve biodiversity? R. E. Gullison Abstract Forest certification provides a means by convincing forest owners to retain forest cover and pro- which producers who meet stringent sustainable forestry duce certified timber on a sustainable basis, rather than standards can identify their products in the marketplace, deforesting their lands for timber and agriculture. 3) At allowing them to potentially receive greater market access present, current volumes of certified forest products are and higher prices for their products. An examination insuBcient to reduce demand to log high conservation of the ways in which certification may contribute to value forests. If FSC certification is to make greater inroads, biodiversity conservation leads to the following con- particularly in tropical countries, significant investments clusions: 1) the process of Forest Stewardship Council will be needed both to increase the benefits and reduce (FSC)-certification generates improvements to manage- the costs of certification. Conservation investors will ment with respect to the value of managed forests for need to carefully consider the biodiversity benefits that biodiversity. 2) Current incentives are not suBcient to will be generated from such investments, versus the attract the majority of producers to seek certification, benefits generated from investing in more traditional particularly in tropical countries where the costs of approaches to biodiversity conservation. improving management to meet FSC guidelines
    [Show full text]
  • Effects of a Windthrow Disturbance on the Carbon Balance of a Broadleaf Deciduous Forest in Hokkaido, Japan
    Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Manuscript prepared for Biogeosciences Discuss. with version 2015/04/24 7.83 Copernicus papers of the LATEX class copernicus.cls. Date: 2 November 2015 Effects of a windthrow disturbance on the carbon balance of a broadleaf deciduous forest in Hokkaido, Japan K. Yamanoi1, Y. Mizoguchi1, and H. Utsugi2 1Hokkaido Research Center, Forestry and Forest Products Research Institute, 7 Hitsujigaoka, Toyohira-ku, Sapporo, 062-8516, Japan 2Forestry and Forest Products Research Institute, Tsukuba, 305-8687, Japan Correspondence to: K. Yamanoi ([email protected]) 1 Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Abstract Forests play an important role in the terrestrial carbon balance, with most being in a car- bon sequestration stage. The net carbon releases that occur result from forest disturbance, and windthrow is a typical disturbance event affecting the forest carbon balance in eastern Asia. The CO2 flux has been measured using the eddy covariance method in a deciduous broadleaf forest (Japanese white birch, Japanese oak, and castor aralia) in Hokkaido, where accidental damage by the strong typhoon, Songda, in 2004 occurred. We also used the biometrical method to demonstrate the CO2 flux within the forest in detail. Damaged trees amounted to 40 % of all trees, and they remained on site where they were not extracted by forest management. Gross primary production (GPP), ecosystem respiration (Re), and net ecosystem production were 1350, 975, and 375 g C m−2 yr−1 before the disturbance and 1262, 1359, and −97 g C m−2 yr−1 2 years after the disturbance, respectively.
    [Show full text]
  • Creating a Forest Garden Working with Nature to Grow Edible Crops
    Creating a Forest Garden Working with Nature to Grow Edible Crops Martin Crawford Contents Foreword by Rob Hopkins 15. Ground cover and herbaceous perennial species Introduction 16. Designing the ground cover / perennial layer 17. Annuals, biennials and climbers Part 1: How forest gardens work 18. Designing with annuals, biennials and climbers 1. Forest gardens Part 3: Extra design elements and maintenance 2. Forest garden features and products 3. The effects of climate change 19. Clearings 4. Natives and exotics 20. Paths 5. Emulating forest conditions 21. Fungi in forest gardens 6. Fertility in forest gardens 22. Harvesting and preserving 23. Maintenance Part 2: Designing your forest garden 24. Ongoing tasks 7. Ground preparation and planting Glossary 8. Growing your own plants 9. First design steps Appendix 1: Propagation tables 10. Designing wind protection Appendix 2: Species for windbreak hedges 11. Canopy species Appendix 3: Plants to attract beneficial insects and bees 12. Designing the canopy layer Appendix 4: Edible crops calendar 13. Shrub species 14. Designing the shrub layer Resources: Useful organisations, suppliers & publications Foreword In 1992, in the middle of my Permaculture Design Course, about 12 of us hopped on a bus for a day trip to Robert Hart’s forest garden, at Wenlock Edge in Shropshire. A forest garden tour with Robert Hart was like a tour of Willy Wonka’s chocolate factory with Mr Wonka himself. “Look at this!”, “Try one of these!”. There was something extraordinary about this garden. As you walked around it, an awareness dawned that what surrounded you was more than just a garden – it was like the garden that Alice in Alice in Wonderland can only see through the door she is too small to get through: a tangible taste of something altogether new and wonderful yet also instinctively familiar.
    [Show full text]
  • Growth Performance of Teak ( Tectona Grandis Linn
    CHOWDHURY, RASHID & AFRAD 245 Tropical Ecology 49 (2): 245-250, 2008 ISSN 0564-3295 © International Society for Tropical Ecology www.tropecol.com Growth performance of Teak ( Tectona grandis Linn. f.) coppice under different regimes of canopy opening MD. QUMRUZZAMAN CHOWDHURY 1* , A.Z.M. MANZOOR RASHID 1 & MD. MASUDUZZAMAN AFRAD 2 1Department of Forestry and Environmental Sciences, Shahjalal University of Science and Technology, Sylhet-3114, Bangladesh 2Bangladesh Forest Department, Bhan Bhaban, Dhaka-1212, Bangladesh Abstract: Growth performance of Tectona grandis coppice was investigated under different canopy openings which is an important reforestation tool. Removal of single tree was done for small canopy opening; two trees for medium, and clear felling for large canopy opening. It was observed that, canopy opening did not affect survival rate and number of sprouts. However, stump height affected the number of sprouts; the maximum number of sprouts was found in 10-20 cm stump height from the ground level. In addition, number of sprouts was correlated (p<0.05) with tree and stump diameter. Both diameter and height of sprouts did not differ significantly in the earlier stage (in 6 months) with the space available due to canopy opening, whereas diameter and height growth of sprouts significantly varied when sprouts were getting old (1 year old and onward). Results indicated the potential of coppice management to restore the gaps in the prevailing plantations. Resumen: El desempeño en el crecimiento de un bosquecillo formado por rebrote de Tectona grandis fue investigado bajo diferentes aperturas del dosel, las cuales son una herramienta importante de reforestación. Para una abertura pequeña se removió un solo árbol; se removieron dos árboles para una abertura mediana, y se realizó un aclareo total del rodal para la abertura grande del dosel.
    [Show full text]
  • California's Hardwood Resources; 1986 November 12- Green, C.B
    Figure 4--Black oak logs on this truck in Butte County, California, indicate a wide range of grades common to California hardwoods. (USDA Forest Service photo) though log quality often was high, drying problems and degrade 1965). These studies have generally followed a standard format thwarted most efforts for manufacturing lumber from this species. using the then current Forest Service rules for hardwood log Another problem was that log grading standards for species grades and National Hardwood Lumber Association rules for in the eastern United States were the only standards available; hardwood lumber grades. Test procedures in these studies standards for western species did not yet exist. A basic rule of account for lumber yield based on "green" grades and estimated thumb for comparing yields based on log grades, first stated by dry volumes (tally) adjusted for a 5 percent loss due to shrinkage Hall (1987), was that the combined grade recovery and value (Malcolm 1962). The yield studies did not follow the boards was 20 to 40 percent lower for the average #1 hardwood sawlog, through the processing steps of kiln drying and surfacing. No given identical exterior appearances and dimensions. determination was made of final recovery in surfaced dry ship- Years of experience by many sawmill processors have shown ping grades, volumes, and values. Consequently, the actual that California hardwoods yield a predominance of lower lum­ amount of degrade and loss during these subsequent manufac­ ber grades (#2 and #3 Common) with limited yields of higher turing steps was not accounted for in the results. quality FAS and Select grades (Chick 1979, Hall 1986, Hecathorn Although these studies were nationally accepted by both 1979, Schmidbauer 1979).
    [Show full text]
  • Managing Deadwood in Forests and Woodlands
    Practice Guide Managing deadwood in forests and woodlands Practice Guide Managing deadwood in forests and woodlands Jonathan Humphrey and Sallie Bailey Forestry Commission: Edinburgh © Crown Copyright 2012 You may re-use this information (not including logos) free of charge in any format or medium, under the terms of the Open Government Licence. To view this licence, visit: www.nationalarchives.gov.uk/doc/open-government-licence or write to the Information Policy Team at The National Archives, Kew, London TW9 4DU, or e-mail [email protected]. This publication is also available on our website at: www.forestry.gov.uk/publications First published by the Forestry Commission in 2012. ISBN 978-0-85538-857-7 Jonathan Humphrey and Sallie Bailey (2012). Managing deadwood in forests and woodlands. Forestry Commission Practice Guide. Forestry Commission, Edinburgh. i–iv + 1–24 pp. Keywords: biodiversity; deadwood; environment; forestry; sustainable forest management. FCPG020/FC-GB(ECD)/ALDR-2K/MAY12 Enquiries relating to this publication should be addressed to: Forestry Commission Silvan House 231 Corstorphine Road Edinburgh EH12 7AT 0131 334 0303 [email protected] In Northern Ireland, to: Forest Service Department of Agriculture and Rural Development Dundonald House Upper Newtownards Road Ballymiscaw Belfast BT4 3SB 02890 524480 [email protected] The Forestry Commission will consider all requests to make the content of publications available in alternative formats. Please direct requests to the Forestry Commission Diversity Team at the above address, or by email at [email protected] or by phone on 0131 314 6575. Acknowledgements Thanks are due to the following contributors: Fred Currie (retired Forestry Commission England); Jill Butler (Woodland Trust); Keith Kirby (Natural England); Iain MacGowan (Scottish Natural Heritage).
    [Show full text]
  • Managing and Regenerating Timber in Bottomland Swamps History
    July 2012 FM-17 Managing and Regenerating Timber in Bottomland Swamps History North Carolina has prime examples of high-quality and productive bottomland hardwood and cypress swamps. These swamps have provided a sustainable source of timber products and wood fiber for more than 200 years, and served as a foundation for the creation of the forest products industry in much of North Carolina. The forests of North Carolina, including hard-to-access bottomland swamps, have been harvested in multiple cycles since the settlement of the state in colonial times. Practically-speaking, it is inconceivable that any appreciable amount of “old growth” or “virgin” timber remains in North Carolina’s swamps, simply due to the numerous harvest cycles that have been conducted through history. The Basics of Bottomland Swamp Forests A diversity of forest tree species are adapted to grow in bottomland swamps. Tree species that are most frequently found in North Carolina’s swamps include (alphabetically): Baldcypress Swamp blackgum / Water tupelo Black willow Swamp chestnut oak Cherrybark oak Sweetgum Green ash Sycamore Red maple Yellow-poplar River birch However, that is not to say that you should expect to see all of these species in every bottomland swamp. On the contrary, the trees in some bottomland swamps can be predominately comprised of only a few species. In addition, North Carolina’s diversity of soils and topography promotes a diverse range in the types of bottomland swamps. The types of bottomland swamps most often found in North Carolina include (alphabetically): Black River Bottom: Bottomland areas of major river systems that originate in the coastal plain.
    [Show full text]